| These projects examined the effects of varying levels of forest disturbance on ectomycorrhizal communities and mushroom fruiting. Ectomycorrhizae (ECM) are symbiotic fungi on tree roots. These fungi extend into the soil to share nutrients and water with the tree, and can protect the tree against stresses such as diseases and toxic metals. Since ectomycorrhizae are critical to forests, we wanted to examine how sensitive ECM communities were to a range of forest disturbance levels. Future projects will address questions on the role of ECM diversity to tree growth and health, and the functional significance of below-ground linkages to tree growth. | ![]() |
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A second issue concerning ECM is the commercial value of their mushrooms, such as the pine mushroom (Tricholoma magnivelare), the golden chanterelle (Cantharellus formosus) and the king bolete (Boletus edulis). As ECM mushrooms, these species are sensitive to timber harvesting. We have examined the effects of small gaps and partial cutting on ECM mushroom diversity and biomass. These studies help explore options forest managers will have in managing the landbase for timber and commercial mushrooms. |
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Available Literature:
Kranabetter, J.M. and Wylie, T. 1998. Ectomycorrhizal community structure across forest openings on naturally regenerated western hemlock seedlings. Can. J. Bot., 76:189-196.
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Abstract: We examined the diversity and distribution of ectomycorrhizal morphotypes on naturally-regenerated western hemlock (Tsuga heterophylla (Raf.) Sarg.) seedlings across small forest openings (50-75 m diameter) in northwest British Columbia. The total and average morphotype richness decreased across the 4-year-old forest openings despite the rapid establishment of western hemlock and lack of soil disturbance. Average fungal richness decreased from 13.1 morphotypes under theforest canopy to 9.6 at the forest edge (27% reduction) and to 7.8 in the forest opening (40% reduction). Cenococcum geophilum, Mycelium radicis | |
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Ectomycorrhizae on hemlock root tip |
atrovirens and Lactarius spp. were the most abundant ectomycorrhizae at each gap position; none of the | |
| ectomycorrhizal fungi found in openings were eliminated by ‘late-stage’ fungi in mature stands. This fungal distribution supports the ‘multi-stage’ concept of ectomycorrhizal succession. Seedlings under the forest canopy had a total of 38 fungal morphotypes in a relatively even distribution pattern that corresponded well to the 'random niche boundary' hypothesis. Fungal distributions were progressively less even for seedlings at the forest edge and opening than for seedlings beneath the canopy, perhaps because reduced fungal diversity and hyphal inoculum had affected the competitive balance of the ectomycorrhizal community. | ||
Kranabetter,
J.M., Hayden, S. and Wright, E.F. 1999. A comparison of
ectomycorrhiza communities from three conifer species planted on forest
gap edges. Can. J. Bot. 77: 1193-1198.
Abstract: We examined the ectomycorrhiza communities
on lodgepole pine (Pinus contorta var. latifolia), white
spruce (Picea glauca), and subalpine fir (Abies lasiocarpa)
seedlings planted together on mature-forest edges in north-western British
Columbia. We examined 32 seedlings of each tree species, grouped
by pairs along the north and south edges of 8 gaps. We found 74 morphotypes
in total, with an average of 52 morphotypes per tree species. Morphotypes
with emanating hyphae or strands made up 60% of the overall ectomycorrhiza
community. Multi-host fungi averaged almost 60% of total morphotypes
in species comparisons, although some of the multi-host fungi appeared
to have tree host preferences. The average community similarity,
based on morphotype abundance, was 52% between conifer species, and 37%
for morphotypes with emanating hyphae or strands. Within planted
groups, between seedlings 1 to 2 m apart, community similarity ranged from
2 to 40% for morphotypes with emanating hyphae or strands. In mature,
mixed forests, the infrequent occurrence of many multi-host ectomycorrhizae
created a wide range in the probability of hyphal linkages between neighbouring
seedlings.
Kranabetter,
J.M. 1999. The effect of refuge trees on a paper birch ectomycorrhiza
community.
Can. J. Bot. 77: 1523 - 1528.
Abstract: Live trees within forest disturbances
could support refugia populations of ectomycorrhiza fungi from which to
reestablish ectomycorrhiza communities during forest succession.
I examined the effectiveness of refuge paper birch trees (Betula papyrifera)
in maintaining a forest ectomycorrhiza community on birch seedlings, both
in clearcuts and forests, in northwest British Columbia. Seedlings
next to refuge birch trees in clearcuts had equal levels of average morphotype
richness and eveness as seedlings next to mature birch trees in forests.
Seedlings outside of the rooting zone of refuge trees had significantly
less average morphotype richness in both clearcuts and forests, decreasing
by 38% and 15%, respectively. The ectomycorrhiza communities were
also more unique (lower community similarity) next to refuge trees than
for seedlings away from refuge trees, especially in clearcuts.
These treatment effects could be explained by differences in the ability
to disperse and establish between early-stage, multi-stage, and late-stage
ectomycorrhiza fungi. The results suggest refuge trees would be effective
in forest management as sources of inocula for multi-stage and late-stage
fungi.
Kranabetter,
J.M. and P. Kroeger. 2001. Ectomycorrhizal mushroom
response to partial cutting in a western hemlock/western redcedar forest.
Can. J. For. Res. 31: 978-987.
Abstract: We examined epigeous ectomycorrhizal
mushroom richness and productivity five years after partial cutting in
a western hemlock (Tsuga heterophylla) - western redcedar (Thuja
plicata) forest of northwestern British Columbia. Mushrooms were
collected throughout the fruiting season (July to October) for three years
from plots with mesic soil conditions and residual basal areas ranging
from 23 to 69 m²/ha for western hemlock, and 0 to 26 m²/ha for
western redcedar. Partial cutting had no apparent effect on mushroom
phenology over the three years. Significant block interactions demonstrated
that reductions in basal area of western hemlock could lead to positive,
neutral and negative responses in mushroom richness, biomass and number
of fruiting bodies. These responses were related to stand structure
and the potential differences in tree vigour after partial cutting.
In addition, there was weak evidence that western redcedar, a host for
vesicular-arbuscular mycorrhiza, had a negative effect on average taxa
richness. The study demonstrated that partial cutting systems could
allow some timber removal without necessarily reducing ectomycorrhizal
mushroom communities.
| Durall, D.M., Jones,
M.D., Wright, E.F., Kroeger, P., and Coates, K.D. 1999. Species
richness of ectomycorrhizal fungi in cutblocks of different sizes in the
interior cedar-hemlock forests of northwestern British Columbia: sporocarps
and ectomycorrhizae. Can. J. For. Res. 29: 1322-1332.
Abstract: We investigated the species richness of ectomycorrhizal fungi based on epigeous sporocarps in an Interior Cedar-Hemlock forest in northwestern British Columbia in gap sizes of 49 to 4526 m2 three to four years following harvest. We also determined ectomycorrhizal diversity on Pinus contorta var. latifolia and Tsuga heterophylla seedlings two years after out-planting. Ectomycorrhizal fungal richness, based on epigeous sporocarps, decreased exponentially as gap size increased. There were sporocarps of 15 species along 475 m of transect in gaps larger than 900 m2, which was approximately 13% of the number of species present in neighboring forests (115 species along 300m of transect). |
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| These data have implications for foresters who would be interested in managing forests for |
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| both timber and edible mushroom harvesting. Ectomycorrhizal richness on seedlings decreased slightly at increasing distances from the edge of the intact forest. The maximum richness was found at 7 m or less from the forest edge for both tree species. The decrease in richness with distance from the forest was associated with an increase in the proportion of Thelephora mycorrhizae in the samples. The number of types of ectomycorrhizae on root systems and the number of species producing epigeous sporocarps were not correlated. These results confirm the importance of sampling both sporocarps and root tips to achieve an accurate estimate of the ectomycorrhizal fungal community in forest ecosystems. | ||
J.M. Kranabetter and J. Friesen 2002. Ectomycorrhizal
community structure on western hemlock (Tsuga heterophylla) seedlings
transplanted from forests into openings. Can. J. Bot. 80:861-868.
Abstract: This study tested whether
mature-forest ectomycorrhizal (ECM) communities could be maintained in
forest openings on seedlings. Naturally-regenerated western hemlock
(Tsuga heterophylla) seedlings were transplanted from mature forests
into openings and the ECM fungal community was compared after two years
with similar seedlings planted back into the forests, or seedlings from
openings planted back into openings. Fewer ECM morphotypes, lower
average richness per seedling, and a steeper, less even species distribution
curve were found, all of which suggest the mature-forest ECM fungal community
changed after transplanting forest seedlings into the openings. The
increased abundance of pioneer fungi such as Thelephora terresteris
suggested many of the mature-forest ECM fungi were unable to maintain or
continue root colonization in openings. Results suggest many mature-forest
ectomycorrhizal fungi require further stand development to maintain enough
rooting density and hyphal contact to persist.
Kranabetter, J.M. 2004. Ectomycorrhizal community effects
on hybrid spruce seedling growth and nutrition in clearcuts. Can. J. Bot.
82: 983-991.
Abstract: A diverse community of ectomycorrhizal
fungi is generally considered beneficial to forest ecosystems, but the
function of ectomycorrhizal communities should be considered within an
ecological context. The growth of hybrid spruce (Picea glauca x sitchensis)
seedlings were compared after transplanting into recent clearcuts, where
soil moisture and nitrogen are typically readily available. The seedlings
had either a 'forest' ectomycorrhizal community (taken from forest gap
edges) or a 'pioneer' ectomycorrhizal community (taken from disturbed road
edges) and were planted at wide and close spacing. After three years,
there was considerable overlap in morphotype distribution and abundance
(64% community similarity between 'forest' and 'pioneer' seedlings), but
height growth was 25% greater for the 'pioneer' seedlings. There
was a reduction in diameter at close spacing, with little difference in
competition effects between ectomycorrhizal communities. There were
no differences detected in foliar nitrogen concentrations, and no evidence
of nitrogen or phosphorus deficiencies. The advantage of fungi such
as Amphinema byssoides, Thelephora terrestris and Laccaria
laccata might be the proliferation of fine roots that allows for the
fullest utilization of abundant soil resources. The results suggest
that the ectomycorrhizal communities arising after clearcut disturbances
are well adapted to these initial soil conditions.
Kranabetter,
J.M. 2005.
Understory conifer seedling response
to a gradient of root and ectomycorrhizal fungal contact.